Status and Distribution of the Gapped Ringed Crayfish, Orconectes neglectus chaenodactylus, in Arkansas
Journal of the Arkansas Academy of Science
Volume 64
Article 24
2010
Status and Distribution of the Gapped Ringed
Crayfish, Orconectes neglectus chaenodactylus, in
Arkansas
Brian K. Wagner
Arkansas Game and Fish Commission,
C. A. Taylor
Illinois Natural History Survey
Mark D. Kottmyer
The Nature Conservancy
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Recommended Citation
Wagner, Brian K.; Taylor, C. A.; and Kottmyer, Mark D. (2010) "Status and Distribution of the Gapped Ringed Crayfish, Orconectes
neglectus chaenodactylus, in Arkansas," Journal of the Arkansas Academy of Science: Vol. 64 , Article 24.
Available at: http://scholarworks.uark.edu/jaas/vol64/iss1/24
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Journal of the Arkansas Academy of Science, Vol. 64 [2010], Art. 24
Status and Distribution of the Gapped Ringed Crayfish,
Orconectes neglectus chaenodactylus, in Arkansas
B.K. Wagner1, C.A. Taylor2, and M.D. Kottmyer3
1
2
Arkansas Game and Fish Commission, 915 E. Sevier Street, Benton, AR 72015
Illinois Natural History Survey, Center for Biodiversity and Ecological Entomology, 1816 S. Oak, Champaign, IL 61820
3
The Nature Conservancy, 675 North Lollar Lane, Fayetteville, AR 72701
Correspondence:
Abstract
Orconectes neglectus chaenodactylus, the gapped
ringed crayfish, is an uncommon and poorly-known,
stream-dwelling crayfish that is endemic to the central
White River basin of Arkansas and Missouri. This
study surveyed a semi-random selection of stream sites
in the Arkansas portion of this range in order to
characterize the crayfish communities and evaluate the
status of O. n. chaenodactylus in Arkansas.
Collections of a total of 1,107 individual crayfish
specimens were made at 45 sites, including 497 O. n.
chaenodactylus from 21 sites.
Orconectes
punctimanus was the crayfish species most commonly
associated with O. n. chaenodactylus, occurring at 71%
of sites occupied by O. n. chaenodactylus. Orconectes
n. chaenodactylus was found in streams not
significantly different from the median characteristics
of streams sampled in the study. It is our opinion that
O. n. chaenodactylus is uncommon in Arkansas, and of
only moderate concern due to its limited distribution in
the state.
Introduction
The ringed crayfish, Orconectes neglectus, was
originally described from Mill Creek in Wabaunsee
County, Kansas (Faxon 1885). It is a medium-sized,
stream-dwelling crayfish, typically growing to a total
size of 30.5 – 96.5 mm (Pflieger 1996). It has broad,
heavy chelae, a rostrum with a trough-like central
depression, and male gonopods with two elongate,
slightly curved processes (Pflieger 1996).
The gapped ringed crayfish, Orconectes neglectus
chaenodactylus, was recognized as a distinct
subspecies based on specimens from White Creek in
Douglas County, Missouri (Williams 1952). It differs
from the nominate subspecies in having chelae with
more slender fingers with a broad gap between the
fingers and a smaller, shorter rostrum (Williams 1952).
In addition to its long-standing recognition based on
morphological characteristics, more recent genetic
studies suggest the possibility that it is a distinct
species (Crandall and Fitzpatrick 1996, Crandall 1998,
Dillman et al. 2007).
This crayfish is a tertiary burrower occupying
cavities excavated under rocks seated in gravel and
coming out at night to forage (Pflieger 1996). Price
and Payne (1979) found females with eggs from midApril to mid-June in North Sylamore Creek, Stone
County, Arkansas. They found the mean size at
maturity to be 13.5 mm CL, based on the minimum
size at which they observed a 50% probability of males
being form-I, and observed that 50% reach this size
during their first summer. Further, they noted adults
molting 4 times in a year, in contrast to the standard
expectation of 2 molts per year. Most adults live 2 to 3
years, with older individuals being rare. Price and
Payne (1984a,b) observed young-of-the-year to appear
in May in North Sylamore Creek and noted no gender
differences in growth.
O. n. chaenodactylus has a limited and poorly
understood distribution. Original work suggested its
endemism to the North Fork White River basin in
Missouri (Williams 1954). It was first collected by
1967 in Arkansas (Robison 2002, Smithsonian lot
USNM131642). Populations were originally thought
to be restricted to the North Fork White River, and
intergrades were hypothesized between it and O. n.
neglectus throughout the remainder of the White River
basin (Hobbs 1989, Pflieger 1996, Williams 1952). It
has subsequently been reported from a few divergent
locations in Arkansas, primarily in the North Fork
White River and Sylamore Creek basins. It has
recently been discovered, due to a suspected
introduction, in the Spring River basin (Rabalais and
Magoulick 2006). Taylor et al. (2007) considered it to
be “vulnerable” and The Nature Conservancy ranks it
as G5T3S2, meaning it is globally secure as a species,
found locally in a restricted range as a subspecies, and
very rare within the state.
The objective of this study was to document the
Journal of the Arkansas Academy of Science, Vol. 64, 2010
115
Published by Arkansas Academy of Science, 2010
115
Journal of the Arkansas Academy of Science, Vol. 64 [2010], Art. 24
B.K. Wagner, C.A. Taylor, and M.D. Kottmyer
diversity and distribution of the crayfish fauna of the
North Fork White and Middle White river basins in
Arkansas and establish baseline distribution and status
of O. n. chaenodactylus.
Methods
Study Area and Site Selection
This study focused on the portions of the North
Fork White and Middle White river basins in northern
Arkansas. Based on the National Hydrology Dataset
(NHD), these hydrologic units comprise 5,045
identified stream segments totaling 97,872 km. The
Arkansas portion of these units includes parts of
Baxter, Cleburne, Fulton, Independence, Izard, Searcy,
Sharp, and Stone counties. Since these areas are
largely in private ownership, road access to sampling
sites was particularly important. U. S. Census Bureau
data on roads in these counties was combined with the
NHD data using ArcMap™ GIS software to identify
stream segments intersected by roads. A random
subset of these segments was selected for sampling by
generating a random number between 0 and 19 as a
start point, and then every 20th segment listed in the
pooled list of accessible stream segments was (...truncated)